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Diet of Breeding Ospreys in the Cape Verde Archipelago,
Northwestern Africa

Author(s) :Samir Martins, Rui Freitas, Luís Palma, and Pedro BejaSource: Journal of Raptor Research, 45(3):244-251. 2011.
Published By: The Raptor Research FoundationDOI: 10.3356/JRR-10-101.1 BioOne () is a a nonprofit, online aggregation of core research in thebiological, ecological, and environmental sciences. BioOne provides a sustainableonline platform for over 170 journals and books published by nonprofit societies,associations, museums, institutions, and presses.
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DIET OF BREEDING OSPREYS IN THE CAPE VERDE ARCHIPELAGO, Departamento de Engenharias e Cieˆncias do Mar, Universidade de Cabo Verde, CP 163 Mindelo, CIBIO, Centro de Investigac¸a˜o em Biodiversidade e Recursos Gene´ticos, Campus Agra´rio de Vaira˜o, Universidade do Porto, Vaira˜o 4485-601, Portugal ABSTRACT.—We studied the diet of breeding Ospreys (Pandion haliaetus) in the Cape Verde archipelagoduring 2006, using prey remains recovered at 21 nests and perches on the islands of Sa˜o Vicente, Santiago,Santa Luzia, Boavista, Branco, and Raso. We identified a total of 1264 individual fish prey items of 35species. Diet was dominated (.80%) by only six fish species, including Trachinotus ovatus, Exocoetus volitans,Aulostomus strigosus, Sparisoma cretense, Sardinella maderensis, and Tylosurus acus. Dominant prey species variedamong islands, but diet similarity was greater between nearby islands. Pelagic species were consumed mostfrequently (.60%) in Boavista and Santa Luzia, whereas demersal reef fish dominated (.50%) in theother islands. The fish consumed were generally large, though there was wide variation in estimated length(20.7–62.2 cm) and weight (49–1117 g). A comparison of Osprey diet with Cape Verde fisheries suggestedthat the potential for conflict is low, due to minimal overlap in the primary species caught. Changes inmarine productivity associated with the ongoing moderate warming of the Canary Current System mayrepresent a threat, though there is considerable uncertainty about the type and magnitude of these effects.
Monitoring of Osprey numbers, breeding success, and diet is required to detect any changes associated withavailability of food sources, and such monitoring may also provide a relatively simple and inexpensivemethod to track long-term changes in littoral fish assemblages.
Osprey; Pandion haliaetus; Cape Verde; diet; foraging ecology; piscivory.
DIETA DE INDIVIDUOS REPRODUCTIVOS DE PANDION HALIAETUS EN EL ARCHIPIE RESUMEN.—Estudiamos la dieta de individuos reproductivos de Pandion haliaetus en el archipie´lago de CaboVerde durante 2006, usando restos de presas recolectados en 21 nidos y perchas en las islas Sa˜o Vicente,Santiago, Santa Luzia, Boavista, Branco y Raso. Identificamos un total de 1264 presas de peces correspon-dientes a 35 especies. La dieta estuvo dominada (.80%) por so´lo seis especies de peces, incluyendoTrachinotus ovatus, Exocoetus volitans, Aulostomus strigosus, Sparisoma cretense, Sardinella maderensis y Tylosurusacus. Las especies dominantes de presas variaron entre las islas, pero la similitud de las dietas fue mayorentre las islas cercanas. Las especies pela´gicas fueron consumidas con mayor frecuencia (.60%) en Boa-vista y Santa Luzia, mientras que los peces de fondo de los arrecifes dominaron (.50%) en otras islas. Lospeces consumidos fueron generalmente grandes, aunque hubo gran variacio peso (49–1117 g) estimado. Una comparacio ´ n de la dieta de P. haliaetus con las pesqueras de Cabo Verde sugirio´ que existe poco potencial de conflicto, debido a la baja superposicio´n en la principal especiecapturada. Los cambios en la productividad marina asociados con el calentamiento moderado en cursodel Sistema de Corriente de las Canarias pueden representar una amenaza, aunque hay una incertidumbreconsiderable sobre el tipo y la magnitud de estos efectos. Se requiere el monitoreo de los nu e´xito reproductivo y de la dieta de P. haliaetus para detectar cualquier cambio asociado con la disponibi-lidad de las fuentes de alimento, y este monitoreo tambie´n puede brindar un me´todo relativamente simpley barato para seguir los cambios a largo plazo en los ensambles de peces de litoral.
1 Present address: Cabo Verde Natura 2000, Rua 1u de Maio, CP 100 Sal Rei, Cabo Verde.
2 Email address: pbeja@mail.icav.up.pt The Osprey (Pandion haliaetus) has a nearly world- mentioned in later studies (Naurois 1987, Ontiveros wide distribution and large population sizes (Poole 2003). Instead, fish of the families Carangidae, 1989), despite dramatic, but transitory, reductions Acanthuridae, Scombridae, and Exocoetidae were in range and numbers due to organochlorine-in- obtained from nests in Santa Luzia and Raso (Naur- duced reproductive suppression during the second ois 1987), and parrotfish of the genus Sparisoma half of the twentieth century (Watts and Paxton were by far the most important prey recorded in 2007, Bai et al. 2009). The global conservation status Boavista (Ontiveros 2003). These preliminary data of Ospreys is thus of Least Concern (BirdLife Inter- suggest that Ospreys in the Cape Verdes may exploit national 2010), though there is evidence that some a wide range of marine fish, though there may be local populations are highly vulnerable to extermi- strong spatial variation in the most important prey nation. This is the case for small and isolated pop- species. We here provide a comprehensive account ulations in the Mediterranean and Macaronesia, of Osprey diet in the Cape Verde archipelago. Spe- where the species is restricted to the islands of Cor- cifically, we describe: (1) prey species and sizes most sica and the Baleares, the North African coast, and frequently consumed by Ospreys, (2) dietary varia- the Atlantic archipelagos of the Canaries and Cape tion across islands, and (3) the fish habitats (pelagic Verde (Thibault et al. 1996, Palacios 2004, Palma et vs. demersal) most often exploited by Ospreys. We al. 2004). Protection of peripheral populations such use our results to identify key trophic resources for as these may be important for the long-term conser- Ospreys in the Cape Verde islands and to discuss the vation of even geographically widespread species conservation implications of potential variations in resource availability due to fisheries and climate With about 70–80 breeding pairs, the Cape Verde archipelago holds the largest Osprey population inthe whole of the Mediterranean and Macaronesia (Palma et al. 2004). Ospreys are largely concentrat- Study Area. The Cape Verde archipelago is made ed in the northern Barlavento (windward) islands up of 10 islands and several islets of volcanic origin group (Santo Anta˜o, Sa˜o Vicente, Santa Luzia, Sa˜o (surface: 4026 km2; coastline: 1050 km) between Nicolau, Branco, Raso, Boavista, and Sal), where the 14u509–17u209N and 22u409–25u309W, about 600 km population appears to be recovering from past de- west of the African mainland (Senegal). Maximum clines due to overharvesting of eggs and nestlings distance between islands (Santo Anta˜o–Maio) is for human consumption (Palma et al. 2004). In the about 280 km. All islands are inhabited except Santa southern Sotavento (leeward) islands (Maio, San- Luzia and the islets. Cape Verde is included in the tiago, Fogo, Rombos, and Brava) the species is African Sahelian arid and semiarid climate regions scarce and seemingly still declining (Palma et al.
and in the Macaronesian biogeographic region 2004). Reasons for these contrasting population siz- (Duarte and Romeiras 2009). The climate is dry es and trends are poorly known, but may be related tropical, with roughly three main seasons: warm at least partly to differences in prey availability dry (May–July), warm wet (August–September), (Naurois 1987). The Barlavento islands are influ- and cold dry (December–April; Medina et al.
enced by the Canary Current System, which brings 2007). Ospreys breed during the cold dry season relatively cold waters rich in nutrients from upwell- (Naurois 1987), when water surface temperature is ing areas in northern Africa (Roy and Cury 2003).
This creates the conditions for high marine produc- Dietary Analysis. We collected fish remains recov- tivity and fish abundance (Roy and Cury 2003), ered from 21 nests and perch sites in January 2006 which in turn may influence Osprey population dis- (Branco and Raso islets) and between April and tribution, density, and breeding success (Harmata June 2006 (islands of Sa˜o Vicente, Santiago, Santa et al. 2007, Bai et al. 2009, Glass and Watts 2009).
Luzia, and Boavista). Sampling was limited by the Despite the value of foraging ecology for under- number of nests in each island (Palma et al. 2004), standing population dynamics and spatial distribu- by difficulties of access of remote nests and perches, tion patterns, little is known about Osprey diet in and by travel constraints between and within is- the Cape Verde islands. Early reports described the lands. Fish remains collected at each sampling site comber (Serranus cabrilla) as the most important were stored in plastic bags, labeled, and frozen for prey of Ospreys in the archipelago (Bannerman future analysis. We identified remains using a refer- and Bannerman 1968), but this species was not ence collection of bones and scales of fish occurring in the Cape Verde archipelago (e.g., Reiner 1996), 67.8%) than demersal species (32.2%; 95% CI: obtained from local fishermen and marine biolo- 32.2–37.4%). The only non-fish items recorded gists. We then estimated the minimum number of were one juvenile cat (Felis catus), one Bulwer’s Pe- individuals of each species represented in a sample trel (Bulweria bulwerii), and one Little Shearwater from the number and sizes of diagnostic bones (Puffinus assimilis boydi), although it was uncertain (e.g., maxillae, premaxillae, operculae, etc.). We al- whether these items were taken as prey or as nest so used bones to estimate the size of fish captured by Ospreys, from regression equations relating bone Comparisons Among Islands. The number of prey size (e.g., width, breadth, maximum length) to fish species recorded per island varied widely across the length and length-weight regressions (S. Martins un- archipelago (Table 2), but there was a tendency for this to be correlated with variation in sample sizes Data Analysis. We quantified diet as the numeric among islands, albeit not significantly so (r 5 0.80, frequency of each prey type, computed as the num- n 5 5, P 5 0.105). Diet diversity was uncorrelated ber of individuals of that prey type relative to the with sample sizes (r 5 0.29, n 5 5, P 5 0.633), with total number of individuals identified (e.g., Beja the lowest value on Santiago and the highest in the 1997). To assess whether Ospreys were feeding on northern group of islands, particularly on Santa Lu- fish living mainly in the water column or near the sea bottom, we classified species as either pelagic or For further analyses of diet composition, we com- demersal according to their main habitat type (Fro- bined fish with percentage numbers ,5% in the ese and Pauly 2010). We used contingency tables category ‘‘other fish’’ (16.6% of individuals identi- (Legendre and Legendre 1998) to assess variation fied). We also combined data from the nearby islets in diet composition among islands. We also used of Branco and Raso (about 6 km), due to small correspondence analysis (CA) to summarize the sample sizes. Analysis revealed a significant dietary spatial patterns of dietary variation (Legendre and variation (x2 5 639.0, df 5 24, P , 0.001), with Legendre 1998). Before CA, we square-root-trans- major differences among islands in dominant prey formed proportional diet composition data to re- species (Table 2). The first two axes extracted from duce the influence of a few prey species that were correspondence analysis accounted for 79% of var- taken very frequently (Legendre and Legendre iation in the data, showing a strong segregation be- 1998). We estimated diet diversity using Shannon’s tween the southern (Santiago), central (Boavista), entropy H (Legendre and Legendre 1998).
and northern (Sa˜o Vicente, Santa Luzia, andBranco/Raso) islands (Fig. 1).
Santiago was characterized by a diet largely dom- Overall Diet Patterns. We recovered prey remains inated by A. strigosus, with T. ovatus and Sardinella from Osprey nests and perches representing 1264 maderensis also making an important dietary contri- individual fishes and 32 species of 24 families (Ta- bution. More than half the fish consumed at Boa- ble 1). Most remains originated from the islands of vista were T. ovatus, though E. volitans and several Boavista (38.3%), Sa˜o Vicente (37.0%), and Santa minor prey species (18) also were taken frequently.
Luzia (18.4%), whereas few were gathered on San- Diet in the northern group was mostly characterized tiago (1.5%), Raso (4.0%), and Branco (0.7%). De- by the high contribution of prey species that were spite the large number of families recorded, nearly generally less represented on Boavista and Santiago, 80% of fish prey belonged to just five families: Car- including E. volitans, S. cretense, and T. acus. Howev- angidae (26.8%), Exocoetidae (16.6%), Aulostomi- er, there were important dietary differences within dae (14.6%), Scaridae (11.2%), and Clupeidae the northern group, with A. strigosus dominating on (10.2%). Likewise, six species with numeric fre- Sa˜o Vicente, S. cretense and T. acus in Santa Luzia, quencies .5% accounted for 83.5% of fish identi- and the ‘‘other fish’’ in Branco/Raso.
fied, including the pompano (Trachinotus ovatus), The proportion of pelagic versus demersal species the tropical two-wing flying fish (Exocoetus volitans), consumed also varied among islands (x2 5 172.6, df the Atlantic cornetfish (Aulostomus strigosus), the 5 4, P , 0.001), with pelagic fish dominating in parrotfish (Sparisoma cretense), the Madeiran sardi- Boavista (86.0%) and Santa Luzia (64.8%). Pelagic nelle (Sardinella maderensis), and the agujon needle- fish were less important than demersal fish on Sa˜o fish (Tylosurus acus; Table 1). Pelagic fish were far Vicente (47.9%), Santiago (42.1%), and the islets of more frequently consumed (65.2%; 95% CI: 62.6– Fish prey species recorded in the diet of Ospreys in the Cape Verde archipelago (January–June 2006), indicating fish family, the main habitat type (P 5 pelagic; D 5 demersal), the percentage of islands where it occurredin the diet (% islands), and the frequency in the diet (% numbers).
Fish Sizes. We obtained data on lengths and sumed a wide variety of pelagic and demersal fish, weights of 162 individual fish prey, including the but only a few species were important in the diet.
four most important species and the surgeonfish This was particularly evident at the scale of indi- (Acanthurus monroviae; Table 3). Fish sizes varied vidual islands, with just 1–3 species accounting for widely, with estimated lengths between 20.7 and .50% of prey consumed on each island. These key 62.2 cm (mean: 38.6 6 8.6 cm [SD]), and weights prey species varied greatly across the archipelago, between 49 and 1117 g (mean: 366 6 211 g [SD]).
though there was a tendency for higher dietary sim- The longest fish captured tended to be A. strigosus, ilarity among nearby islands, probably due to differ- but they usually had a low mass. The heaviest fish entiation in fish assemblage structure associated with geographic distance (Medina et al. 2007).
Most fish prey recorded at Cape Verde have been rarely or never found in Osprey diets elsewhere, As in other studies (e.g., Poole 1989, Francour likely reflecting the specificity of fish communities and Thibault 1996, Cartron and Molles 2002, Clancy around the archipelago (Floeter et al. 2008). Nev- 2005), Ospreys in the Cape Verde archipelago con- ertheless, the species most frequently consumed at Variation in frequency (% of total numbers), number of prey species, and diversity of Osprey diet among islands of the Cape Verde archipelago (January–June 2006); n 5 number of fish prey items identified.
FREQUENCY OF FISH SPECIES IN THE DIET (%) BY ISLAND Cape Verde shared some ecological and morpho- dant where the rocky coast plunges abruptly to the logical similarities with those taken by Ospreys feed- depths (Safriel et al. 1985), which may explain their ing in other subtropical and tropical marine waters.
high consumption in islands with very narrow rocky For example, the fish most commonly captured by Ospreys in the Tiran Island (Red Sea) was the blue- fish (S. cretense) and surgeonfish (Acanthurus spp.) are spotted cornetfish (Fistularia commersonii; Safriel et slow-swimming fish that also occur in shallow water al. 1985), which is a Syngnathiforme broadly similar along rocky shores, which may make them highly vul- to A. strigosus which was an important prey on San- nerable to Ospreys. Among the pelagic species, the tiago and Sa˜o Vicente (Cape Verde). Likewise, nee- high consumption of needlefish is likely explained by dlefish such as Tylosurus spp. were consumed fre- the habit of this predator of remaining close to the quently in Cape Verde (Santa Luzia), the Red Sea water surface, nearly motionless, with the body point- (Safriel et al. 1985), the Gulf of California (Cartron ing slightly downwards (Safriel et al. 1985).
and Molles 2002), and the Arabian Gulf (Beech The estimated mass of fish taken most frequently 2003). In contrast to these species, it is noteworthy by Ospreys at the Cape Verdes Islands was generally that mullets (Mugilidade) were very rarely con- large compared to that in other inland and marine sumed at Cape Verde, though they are an important areas (Poole 1989). For example, in Corsica, 94% of part of Osprey diet along the nearby coast of Sene- mullet weighed 180–310 g (mean 5 235 g; Francour gal (Prevost 1982), as they are for many Ospreys and Thibault 1996), whereas 45.1% of fish prey feeding along tropical and subtropical coasts (Car- weighed .300 g in the present study. The greater tron and Molles 2002, Clancy 2005), and in the proportion of large fish observed in this study is clos- Mediterranean (Francour and Thibault 1996). This er to that recorded in the Red Sea (Safriel et al. 1985) was probably due to the scarcity of mullets in the and, to a lesser extent, in New South Wales, Australia (Clancy 2005). This result suggests that feeding con- Factors influencing prey selection by Ospreys in ditions may be particularly favorable in the Cape Cape Verde are unknown at present, due to the Verde archipelago, as large prey is generally believed limited information about coastal fish abundance to be the most profitable for breeding Ospreys (Glass and distribution (but see Medina et al. 2007). How- and Watts 2009). Despite this general pattern, diet ever, a combination of abundance and susceptibility on Santiago was largely dominated by A. strigosus, to capture probably influenced diet composition, as which is a fish with a long body but with low mass.
found elsewhere (Poole 1989). For instance, cornet- This, together with the low dietary diversity recorded, fish may be easily captured because they occur in may indicate that food resources may be less favor- shallow reefs and rocky habitats, where they rest, able on Santiago than elsewhere, which was in agree- immobile, near the bottom to ambush their prey (Sa- ment with the small size of the Osprey population friel et al. 1985). These fish may be particularly abun- Biplot of a correspondence analysis (CA) of Osprey diet composition in the Cape Verde archipelago (Jan- uary–June 2006). Species matrix includes species with .50 identified individuals, and combines the remaining prey in an‘‘other fish’’ category. Data from the nearby islets of Raso and Branco were combined due to small sample sizes. Islandsare represented by filled circles; fish species by open squares.
Conservation Implications. A sustainable Osprey 1985, Clancy 2005). We compared the primary spe- population requires the maintenance of an abun- cies of demersal fish caught by Cape Verde commer- dant food supply, as this strongly influences popu- cial fisheries (Medina et al. 2007) to Osprey diet lation density and breeding success (Harmata et al.
documented in our study, and found the only over- 2007, Bai et al. 2009, Glass and Watts 2009). In Cape lap to be A. monroviae, a fish species that contributed Verde, where large reef and littoral pelagic fish only 2.1% to the overall Osprey diet. Thus, overfish- make up the bulk of Osprey diet, maintenance of ing is unlikely to threaten the population at present, large stocks of these species will help preserve the although concentration of fishing effort at the local Osprey population. One of the potential threats to scale could still influence prey availability for partic- Ospreys could thus be overfishing (e.g., Safriel et al.
Estimated mean (6SD) and range of lengths and masses of fish prey species recorded in the diet of Ospreys in the Cape Verde archipelago (January–June 2006).
Climate change may represent a potentially more BIRDLIFE INTERNATIONAL. 2010. Species factsheet: Pandion serious threat for the Osprey in Cape Verde, due to haliaetus. http://www.birdlife.org (last accessed 20 Sep- potential reductions in marine productivity and fish biomass associated with the ongoing moderate CARTRON, J.-L.E. AND M.C. MOLLES, JR. 2002. Osprey diet along the eastern side of the Gulf of California, Mexi- warming of the Canary Current System (Behrenfeld co. Western North American Naturalist 62:249–252.
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Received 8 November 2010; accepted 26 March 2011 ICBP Technical Publication No. 3, Cambridge, U.K.

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